Skip to main content

Advertisement

Log in

LCI modelling approaches applied on recycling of materials in view of environmental sustainability, risk perception and eco-efficiency

  • LCI MODELLING
  • Published:
The International Journal of Life Cycle Assessment Aims and scope Submit manuscript

Abstract

Purpose and scope

Two ISO-compliant approaches on modelling the recycling of plastics and metals are frequently applied in life cycle assessment case studies and intensively debated: the recycled content or cutoff approach and the end of life recycling or avoided burden approach. This paper discusses the two approaches from three different perspectives: (1) the kind of sustainability concept served, (2) the risk perception involved and (3) the eco-efficiency indicators resulting from the two approaches.

Results and discussion

The analysis shows that the recycled content approach serves the strong sustainability concept. It is based on a risk-averse attitude and results in higher eco-efficiency of metal scrap recycling as compared to primary metal manufacture. The end of life recycling approach serves the weak sustainability concept (losses in natural capital can be compensated by man-made capital). It corresponds to a risk-seeking attitude and results in higher eco-efficiency of primary metal manufacture as compared to secondary metal production.

Conclusions

It is concluded that a harmonisation of the approaches is hardly possible due to the value choices involved. It is the task of (private and public) life cycle assessment commissioners to decide on the appropriate modelling approach. National authorities may have a rather long-term and risk-averse perspective, whilst industries may prefer a short-term perspective leading them to select the recycled content and end of life recycling approach, respectively. Life cycle inventory databases need to be flexible to serve such opposing perspectives and to enable practitioners to adapt the modelling approaches according to the needs of the commissioner.

This is a preview of subscription content, log in via an institution to check access.

Access this article

Price excludes VAT (USA)
Tax calculation will be finalised during checkout.

Instant access to the full article PDF.

Fig. 1

Similar content being viewed by others

Notes

  1. Seven million tons relative to 34.4 million tons in 2003 and 13 million tons relative to 51 million tons in 2020.

  2. Future generations may argue with the sunk cost argument that the emissions to manufacture primary aluminium happened in the past and can no more be influenced. Hence, there is no reason to take past emissions into considerations in their decisions.

References

  • Anonymous (2006) Declaration by the metals industry on recycling principles. Int J Life Cycle Assess 12:59–60

    Google Scholar 

  • Curran M-A (2006) Co-product and input allocation approaches for creating life cycle inventory data: a literature review. Int J Life Cycle Assess 12:65–78

    Google Scholar 

  • Curran MA (2008) Development of life cycle assessment methodology: a focus on co-product allocation. Erasmus University Rotterdam, Rotterdam

    Google Scholar 

  • EAA (2000) Environmental profile report for the European aluminium industry, April 2000. European Aluminium Association, Brussels

    Google Scholar 

  • ecoinvent Centre (2006) ecoinvent data v1.3. Final ecoinvent reports no. 1-16. Swiss Centre for Life Cycle Inventories, Duebendorf. ISBN 3-905594-38-2

    Google Scholar 

  • Ekvall T, Tillmann A-M (1997) Open-loop recycling: criteria for allocation procedures. Int J Life Cycle Assess 2:155–162

    Article  Google Scholar 

  • Ekvall T, Weidema B (2004) System boundaries and input data in consequential life cycle inventory analysis. Int J Life Cycle Assess 9:161–171

    Article  Google Scholar 

  • Frischknecht R (1994): Allocation—an issue of valuation? In: Huppes G, Schneider F (eds) European Workshop on Allocation in LCA. Society of Environmental Toxicology and Chemistry, SETAC, 24–25 February 1994, Leiden, The Netherlands, pp 122–131

  • Frischknecht R (2000) Allocation in life cycle inventory analysis for joint production. Int J Life Cycle Assess 5:85–95

    Article  Google Scholar 

  • Frischknecht R (2006) Notions on the design and use of an ideal regional or global LCA database. Int J Life Cycle Assess 11:40–48

    Article  Google Scholar 

  • Guinée JB, Heijungs R, Huppes G (2004) Economic allocation: examples and derived decision tree. Int J LCA 9:23–33

    Article  Google Scholar 

  • Heijungs R, Frischknecht R (1998) On the nature of the allocation problem. Int J Life Cycle Assess 3:321–332

    Article  Google Scholar 

  • Hertwich E, Hammitt JK, Pease WS (2000) A theoretical foundation for life-cycle assessment: recognizing the role of values in environmental decision making. J Ind Ecol 4:13–28

    Article  Google Scholar 

  • Hofstetter P, Baumgartner W, Scholz R (2000) Modelling the valuesphere and the ecosphere: integrating the decision makers’ perspectives into LCA. Int J LCA 5:161–175

    Article  Google Scholar 

  • ISO (International Organization for Standardization) (2006a) Environmental management—Life cycle assessment—Principles and framework. ISO 14040:2006; Second Edition 2006-06, Geneva

  • International Organization for Standardization (ISO) (2006b) Environmental management—Life cycle assessment—Requirements and guidelines. ISO 14044:2006; First edition 2006-07-01, Geneva

  • Kicherer A, Schaltegger S, Tschochohei H, Ferreira Pozo B (2007) Eco-efficiency. Combining life cycle assessment and life cycle costing via normalization. Int J Life Cycle Assess 12:537–543

    Article  CAS  Google Scholar 

  • Kim S, Hwang T, Lee K-M (1997) Allocation for cascade recycling system. Int J LCA 4:217–222

    Article  Google Scholar 

  • Klöpffer W (1996) Allocation rule for open-loop recycling in life cycle assessment—a review. Int J Life Cycle Assess 1:27–31

    Article  Google Scholar 

  • Martchek K (2006) Modelling more sustainable aluminium. Int J Life Cycle Assess 11:34–37

    Article  Google Scholar 

  • Neumayer E (2003) Weak versus strong sustainability: exploring the limits of two opposing paradigms. Edward Elgar, Cheltenham

    Google Scholar 

  • SETAC (1993): Guidelines for life-cycle assessment: a “Code of Practice”. SETAC Workshop. Society of Environmental Toxicology and Chemistry (SETAC), Brussels, Belgium and Pensacola (Florida, USA). Sesimbra, Portugal, 31 March–3 April 1993

  • Weidema B (2001) Avoiding co-product allocation in life-cycle assessment. J Ind Ecol 4:11–33

    Article  Google Scholar 

  • Werner F (2002) Interdependencies between LC-modelling and the use of LCA in product design-related decision situations. PhD thesis, ETHZ, Zürich

  • Werner F, Richter K (2000) Economic allocation in LCA: a case study about aluminium window frames. Int J LCA 5:79–83

    Article  Google Scholar 

  • Yamada H, Daigo I, Matsuno Y, Adachi Y, Kondo Y (2006) Application of Markov chain model to calculate the average number of times of use of a material in society. An allocation methodology for open-loop recycling. Part 1: methodology development. Int J Life Cycle Assess 11:354–360

    Article  Google Scholar 

Download references

Author information

Authors and Affiliations

Authors

Corresponding author

Correspondence to Rolf Frischknecht.

Additional information

Responsible editor: Hans-Jürgen Garvens

Rights and permissions

Reprints and permissions

About this article

Cite this article

Frischknecht, R. LCI modelling approaches applied on recycling of materials in view of environmental sustainability, risk perception and eco-efficiency. Int J Life Cycle Assess 15, 666–671 (2010). https://doi.org/10.1007/s11367-010-0201-6

Download citation

  • Received:

  • Accepted:

  • Published:

  • Issue Date:

  • DOI: https://doi.org/10.1007/s11367-010-0201-6

Keywords

Navigation